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EC number: 271-411-2 | CAS number: 68555-06-6 An inorganic pigment that is the reaction product of high temperature calcination in which chromium (III) oxide, iron (III) oxide, and manganese (III) oxide in varying amounts are homogeneously and ionically interdiffused to form a crystalline matrix of spinel.
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Adsorption / desorption
Administrative data
- Endpoint:
- adsorption / desorption, other
- Remarks:
- monitoring data in water and sediment
- Type of information:
- other: Calculation of Kp values based on environmental field data
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see "Remark"
- Remarks:
- Kp-values are based on reliable field data of concentration levels in water and sediment; no standard guideline test was conducted to generate Kp-values. Kp-values are calculated based on the hypothesis that equilibrium exists between the baseline levels in water and in sediment.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Reference
- Endpoint:
- monitoring data
- Type of information:
- other: report
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- Evaluation and summary of high quality environmental geochemical data for Europe, which is provided by the Forum of European Geological Surveys (FOREGS) and the European Geochemical Mapping of Agricultural and Grazing Land Soil (GEMAS), with respect to chromium concentrations in stream water, stream sediment and topsoil, as well as in agricultural soil and grazing land.
- GLP compliance:
- no
- Type of measurement:
- other: Geochemical background and ambient chromium concentrations in different environmental compartments across Europe
- Media:
- other: Natural stream water, stream sediment and topsoil, as well as agricultural and grazing land soils
- Details on sampling:
- FOREGS and GEMAS data for EU-27 countries plus UK and Norway were considered, i.e. data from non-EEA countries such as Albania, Bosnia and Switzerland were excluded from further analysis.
FOREGS:
- The FOREGS sampling grid was based on GTN grid cells developed for Global Geochemical Baseline mapping. This grid divides the entire land surface into 160 km x 160 km cells covering an area of 4,500,000 km2.
- Sampling methodology, preparation and analysis are described by Salminen et al. (2005).
- FOREGS data for EU-27 countries plus UK and Norway were considered, i.e. data from non-EEA countries such as Albania and Switzerland were excluded from further analysis.
- A total of 795 stream water samples and 832 sediment samples were processed in the FOREGS-program, including 734 paired samples, i.e. samples with the same coordinates for the sampling location of stream water and sediment.
- The FOREGS dataset reports chromium concentrations for 825 topsoil samples. A topsoil sample was taken at each site from 0-25 cm (excluding material from the organic layer where present).
- High quality and consistency of the obtained data were ensured by using standardised sampling methods and by treating and analysing all samples in the same laboratory of each country.
GEMAS:
- Samples from 33 out of 38 European countries were analysed to develop a suitable harmonised geochemical data base for soils. The sampling started in the spring 2008 and the first four months of 2009.
- The whole GEMAS project area of 5,600,000 km2 was divided into a grid with 50 km x 50 km cells.
- To generate harmonised data sets, all project samples were processed by a central sample preparation facility in Slovakia.
- GEMAS data for EU-27 countries plus UK and Norway were considered, i.e. data from non-EEA countries such as Bosnia and Switzerland were excluded from further analysis.
- The GEMAS dataset reports chromium concentrations of 1,867 samples from the regularly ploughed layer (Ap-horizon) of agricultural land (arable land; 0-20 cm) and of 1,781 samples from the top layer of grazing land (soil under permanent grass cover; 0-10 cm) sampled on a grid across Europe. - Conclusions:
- Representative background or ambient concentrations of chromium in environmental compartments are tabulated below:
compartment, unit, concentration (50th P), concentration (95th P)
background stream water, µg/L Cr, 0.4, 1.8
background stream water sediment, mg/kg Cr, 21.0, 63.0
background topsoil, mg/kg Cr, 22.0, 69.8
agricultural soil, mg/kg Cr, 19.9, 67.2
grazing land soil, mg/kg Cr, 19.8, 67.8
Based on the FOREGS dataset, the 95th percentile of 1.8 µg/L can be regarded as representative background concentration for dissolved chromium in European surface waters and the 95th percentile of 63.0 mg/kg as representative background concentration of European stream sediments. Regarding the respective partitioning between sediment and water, a European median log Kp value of 4.75 is derived.
Based on the FOREGS dataset, the 95th percentile of 69.8 mg/kg can be regarded as representative background concentration of chromium in topsoil of EU countries. Representative chromium concentrations (95th percentile) of agricultural and grazing land soil (i.e. ambient levels) amount to 67.2 and 67.8 mg/kg, respectively, according to the GEMAS dataset.
FOREGS DATABASE STREAM WATER/SEDIMENT:
- Sampled stream water and sediments cover a wide range of environmental conditions. Water parameters such as pH, hardness and organic carbon concentrations extend over several magnitudes. Chromium water levels range from < 0.01 (< LOQ) to 43.0 µg/L with 5th, 50th and 95th percentiles of 0.06, 0.4 and 1.8 µg/L, respectively.
- In the sediment, chromium concentrations range from 2.0 to 1,748.0 mg/kg with 5th, 50th and 95th percentiles of 6.0, 21.0 and 63.0 mg/kg, respectively (Table 1).
-Taking into account the high quality and representativeness of the data set, the 95th percentile of 1.8 µg/L can be regarded as representative background concentration for dissolved chromium in European surface waters and the 95th percentile of 63.0 mg/kg as representative background concentration of chromium in European stream sediments.
-Regarding the partitioning of chromium in the water column, stream water/sediment partition coefficients range from 1,080 to 4,800,000 L/kg. Since FOREGS sampled on a grid aiming to equally represent geochemical baseline concentrations across Europe,a European median log Kp value of 4.75 is derived.
Table 1: Water parameters and chromium concentrations of stream sediment and stream water and respective partitioning.
Parameter |
# |
Unit |
Min. |
Max. |
5th P |
50th P |
95th P |
|
water |
pH 1 |
726 2 |
- |
9.80 |
4.50 |
8.50 |
7.70 |
6.10 |
water |
Ca |
734 |
mg/L |
0.23 |
592.00 |
1.60 |
42.28 |
144.21 |
water |
Cl |
734 |
mg/L |
0.14 |
4,560.00 |
0.49 |
8.95 |
69.08 |
water |
HCO3 |
7323 |
mg/L |
0.69 |
1,804.42 |
5.34 |
128.01 |
370.00 |
water |
K |
734 |
mg/L |
< 0.01 |
182.00 |
0.14 |
1.62 |
9.80 |
water |
Mg |
734 |
mg/L |
0.05 |
230.00 |
0.46 |
6.15 |
36.81 |
water |
Na |
734 |
mg/L |
0.23 |
4,030.00 |
1.00 |
6.66 |
48.30 |
water |
NO3 |
734 |
mg/L |
< 0.04 |
107.00 |
< 0.04 |
3.05 |
39.91 |
water |
DOC |
732 4 |
mg/L |
< 0.50 |
57.94 |
0.60 |
4.84 |
23.11 |
water |
SO42- |
734 |
mg/L |
< 0.30 |
2,420.00 |
1.18 |
16.79 |
164.56 |
water |
Cr |
734 |
µg/L |
< 0.01 |
43.03 |
0.06 |
0.38 |
1.81 |
sediment |
Cr |
734 |
mg/kg |
2.00 |
1,748.00 |
6.00 |
21.00 |
63.00 |
Partitioning (Kp) |
Cr (sed/water) |
734 |
L/kg |
1,080 |
4,800,000 |
8,570 |
56,119 |
390,841 |
Log Kp |
Cr (sed/water) |
734 |
- |
3.03 |
6.68 |
3.93 |
4.75 |
5.59 |
1 Statistics are based on H+ concentrations rather than pH.
2 Removal of 2 outliers < pH 4.3 and 6 negative values.
3 Removal of 2 outliers < 0.01.
4 Removal of 1 outlier > 70 mg/L and 1 negative values.
FOREGS DATABASE Background soil concentrations
- Sampled soils cover a wide range of environmental conditions. Soil parameters, including pH and TOC, cover several magnitudes.
- Baseline chromium levels in topsoil range from 1.0 to 2,340.0 mg/kg with5th, 50th and 95th percentiles of 5.0, 22.0 and 69.8 mg/kg, respectively (see Table 2).
- Taking into account the high quality and representativeness of the data set, the 95th percentile of 69.8 mg/kg can be regarded as representative background concentration of chromium in topsoil of EU countries.
Table 2: Concentrations of chromium in topsoil samples.
Parameter |
Unit |
# |
Min. |
Max. |
5th P |
50th P |
95th P |
pH 1 |
- |
798 |
7.55 |
3.38 |
7.31 |
5.49 |
4.29 |
TOC |
% |
805 |
0.07 |
46.61 |
0.55 |
1.72 |
5.87 |
Cr |
mg/kg |
825 |
1.00 |
2,340.00 |
5.00 |
22.00 |
69.80 |
1 Statistics are based on H+ concentrations rather than pH.
GEMAS DATABASE AGRICULTURAL AND GRAZING LAND SOIL CONCENTRATIONS:
- Chromium levels of agricultural soil range from 0.40 to 696.02 mg/kg with 5th, 50th and 95th percentiles of 4.2, 19.9 and 67.2 mg/kg, respectively (see Table 3). In grazing land, soil concentrations of chromium range from 0.8 to 576.7 mg/kg with 5th, 50th and 95th percentiles of 3.9, 19.8 and 67.8 mg/kg, respectively (see Table 4).
Table 3: Agricultural soil concentrations.
Parameter |
Unit |
Method |
# |
Min. |
Max. |
5th P |
50th P |
95th P |
CEC |
meq/100g |
AAS |
1,867 |
1.80 |
48.30 |
6.10 |
15.80 |
33.30 |
pH (CaCl2) |
pH |
pH-meter |
1,867 |
3.32 |
7.98 |
4.14 |
5.71 |
7.45 |
TOC |
% |
IR |
1,854 |
0.40 |
46.00 |
0.70 |
1.70 |
5.67 |
Chromium |
mg/kg |
AR |
1,867 |
0.40 |
696.02 |
4.16 |
19.87 |
67.16 |
Chromium |
mg/kg |
XRF |
1,867 |
2.00 |
6,133.00 |
14.00 |
58.00 |
191.00 |
Chromium |
mg/kg |
MMI |
1,867 |
< 0.001 |
1.30 |
0.01 |
0.07 |
0.26 |
Table 4: Grazing land soil concentrations.
Parameter |
Unit |
Method |
# |
Min. |
Max. |
5th P |
50th P |
95th P |
CEC |
meq/100g |
AAS |
1,781 |
2.54 |
49.88 |
8.27 |
17.96 |
37.74 |
pH (CaCl2) |
pH |
pH-meter |
1,780 |
3.26 |
8.06 |
4.03 |
5.38 |
7.45 |
TOC |
% |
IR |
1,780 |
0.41 |
49.00 |
0.94 |
2.80 |
11.05 |
Chromium |
mg/kg |
AR |
1,781 |
0.78 |
576.74 |
3.87 |
19.75 |
67.82 |
Chromium |
mg/kg |
XRF |
1,781 |
2.00 |
6,594.00 |
13.00 |
59.00 |
187.00 |
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 005
- Report date:
- 2005
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 021
- Report date:
- 2021
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Evaluation of high quality environmental geochemical data for Europe, which is provided by the Forum of European Geological Surveys (FOREGS), with respect to chromium (Cr) concentrations in stream water and stream sediment. Baseline levels of chromium in water and sediment were determined in 734 paired sample locations. Assuming equilibrium between both environmental compartments, site-specific partitioning coefficients (Kp) were derived.
- GLP compliance:
- no
- Type of method:
- other: field data of baseline levels in water and sediment
- Media:
- sediment
Test material
- Reference substance name:
- not applicable
- IUPAC Name:
- not applicable
- Test material form:
- other: elemental concentrations
- Details on test material:
- natural occuring chromium
Constituent 1
- Radiolabelling:
- no
Study design
- Test temperature:
- environmental relevant temperatures
Batch equilibrium or other method
- Analytical monitoring:
- yes
- Details on sampling:
- FOREGS:
- The FOREGS sampling grid was based on GTN grid cells developed for Global Geochemical Baseline mapping. This grid divides the entire land surface into 160 km x 160 km cells covering an area of 4,500,000 km2.
- Sampling methodology, preparation and analysis are described by Salminen et al. (2005).
- FOREGS data for EU-27 countries plus UK and Norway were considered, i.e. data from non-EEA countries such as Albania and Switzerland were excluded from further analysis.
- A total of 795 stream water samples and 832 sediment samples were processed in the FOREGS-program, including 734 paired samples, i.e. samples with the same coordinates for the sampling location of stream water and sediment.
- High quality and consistency of the obtained data were ensured by using standardised sampling methods and by treating and analysing all samples in the same laboratory of each country.
Results and discussion
Partition coefficientsopen allclose all
- Key result
- Phase system:
- sediment-water
- Type:
- log Kp
- Value:
- 4.75 dimensionless
- Remarks on result:
- other: European median (50th percentile) log Kp
- Key result
- Phase system:
- sediment-water
- Type:
- Kp
- Value:
- 56 119 L/kg
- Remarks on result:
- other: European median (50th percentile) partition coefficient (Kp)
Results: Batch equilibrium or other method
- Adsorption and desorption constants:
- The monitoring stream water and sediment data show that chromium (Cr) concentrations of sediments range from 2.0 to 1,748.0 mg/kg, while dissolved Cr concentrations in the water column of European stream waters range from < 0.01 (< LOQ) to 43.0 µg/L. Regarding the partitioning of Cr in the water column, stream water/sediment partition coefficients ranged from 1,080 to 4,800,000 L/kg. Since FOREGS sampled on a grid aiming to equally represent geochemical baseline concentrations across Europe, the 50th percentile log Kp for Cr across Europe was determined to be 4.75 (56,119 L/kg; Table below).
Any other information on results incl. tables
Table: Water parameters and chromium concentrations of stream sediment and stream water and respective partitioning.
Parameter |
# |
Unit |
Min. |
Max. |
5th P |
50th P |
95th P |
|
water |
pH 1 |
726 2 |
- |
9.80 |
4.50 |
8.50 |
7.70 |
6.10 |
water |
Ca |
734 |
mg/L |
0.23 |
592.00 |
1.60 |
42.28 |
144.21 |
water |
Cl |
734 |
mg/L |
0.14 |
4,560.00 |
0.49 |
8.95 |
69.08 |
water |
HCO3 |
7323 |
mg/L |
0.69 |
1,804.42 |
5.34 |
128.01 |
370.00 |
water |
K |
734 |
mg/L |
< 0.01 |
182.00 |
0.14 |
1.62 |
9.80 |
water |
Mg |
734 |
mg/L |
0.05 |
230.00 |
0.46 |
6.15 |
36.81 |
water |
Na |
734 |
mg/L |
0.23 |
4,030.00 |
1.00 |
6.66 |
48.30 |
water |
NO3 |
734 |
mg/L |
< 0.04 |
107.00 |
< 0.04 |
3.05 |
39.91 |
water |
DOC |
732 4 |
mg/L |
< 0.50 |
57.94 |
0.60 |
4.84 |
23.11 |
water |
SO42- |
734 |
mg/L |
< 0.30 |
2,420.00 |
1.18 |
16.79 |
164.56 |
water |
Cr |
734 |
µg/L |
< 0.01 |
43.03 |
0.06 |
0.38 |
1.81 |
sediment |
Cr |
734 |
mg/kg |
2.00 |
1,748.00 |
6.00 |
21.00 |
63.00 |
Partitioning (Kp) |
Cr (sed/water) |
734 |
L/kg |
1,080 |
4,800,000 |
8,570 |
56,119 |
390,841 |
Log Kp |
Cr (sed/water) |
734 |
- |
3.03 |
6.68 |
3.93 |
4.75 |
5.59 |
1 Statistics are based on H+ concentrations rather than pH.
2 Removal of 2 outliers < pH 4.3 and 6 negative values.
3 Removal of 2 outliers < 0.01.
4 Removal of 1 outlier > 70 mg/L and 1 negative values.
Applicant's summary and conclusion
- Conclusions:
- Reliable baseline levels of chromium in 734 pristine water/sediment samples collected across Europe were determined. Sampling and analytical procedures are considered adequate and resulted in reliable data. Assuming equilibrium between the typical concentration in water and sediment, relevant log Kp-values were generated. Data are therefore considered useful for the determination of a relevant partition coefficient for the sediment compartment. FOREGS sampled on a grid aiming to equally represent geochemical baseline concentrations across Europe. The 50th percentile of chromium concentrations were considered representative and amount to 21.0 mg/kg sediment and 0.4 µg/L stream water, respectively, resulting in a log Kp for partitioning of chromium in European sediment/freshwater of 4.75.
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